Rico é aquele que sabe ter o suficiente. Lao Tze
ISSN 1678-0701 · Volume XXII, Número 90 · Março-Maio/2025
Início Cadastre-se! Procurar Área de autores Contato Apresentação(4) Normas de Publicação(1) Artigos(3) Podcast(1) Dicas e Curiosidades(1) Reflexão(2) Iniciativas Empresariais Sustentáveis(7) Para Sensibilizar(1) Dinâmicas e Recursos Pedagógicos(5) Entrevistas(2) Culinária(2) Divulgação de Eventos(16) O que fazer para melhorar o meio ambiente(1) Sugestões bibliográficas(2) Educação(1) Breves Comunicações(1) Reportagem(3) Soluções e Inovações(2) Educação e temas emergentes(3) Ações e projetos inspiradores(17) Cidadania Ambiental(1) A Natureza Inspira(1) Notícias(20) Relatos de Experiências(7)   |  Números  
Artigos
14/03/2025 (Nº 90) VEGETATED COASTAL ECOSYSTEMS: ENVIRONMENTAL PERCEPTION OF USERS OF THE NORTHERN BRAZILIAN COASTLINES
Link permanente: http://revistaea.org/artigo.php?idartigo=5251 
  

ECOSSISTEMAS COSTEIROS VEGETADOS: PERCEPÇÃO AMBIENTAL DOS USUÁRIOS DO LITORAL NORTE DO BRASIL



Rory Romero de Sena Oliveira1, Danielly Brito de Oliveira2

roryengpesca.s@gmail.com

1Universidade Federal do Pará, Núcleo de Ecologia Aquática e Pesca da Amazônia, Belém, PA, Brazil

2Universidade Federal do Sul e Sudeste do Pará, Instituto de Estudos do Xingu, São Félix do Xingu, Brazil



Resumo: As formações vegetais litorâneas brasileiras são caracterizadas, principalmente, por áreas de apicum, marismas e florestas de manguezais. Tais vegetações são consideradas “ecossistemas-chaves”, devido a conectividade com ecossistemas adjacentes, proporcionando funcionalidade ótima, e ainda favorecendo uma infinidade de organismos e de pessoas que os utilizam. O objetivo do estudo foi avaliar o nível de conhecimento e de percepção ambiental a cerca das vegetações costeiras (i.e., mangues, marismas e apicum) entre os frequentadores da região norte do Brasil. O questionário semiestruturado utilizado foi dividido em três partes relacionadas com: I) informações pessoais, II) comportamento em relação aos problemas ambientais observados, e III) percepção ecológica desses problemas. Um total de 70 pessoas responderam ao questionário online, dentre esses 50% são usuários frequentes das praias do norte brasileiro, 35.7% raramente frequentam, e 14.5% nunca foram ao litoral norte. Os resultados demonstram que uma parcela significativa dos frequentadores do litoral norte entrevistados, desconhecia ações educativas para evitar ou minimizar os impactos ambientais nas praias, principalmente, para os habitats vegetados. Palavras-chave: descarte impróprio; praias arenosas; fauna associadas; educação ambiental; Costa Amazônica

Abstract: The Brazilian coastal plant formations are mainly characterized by areas of apicum, saltmarshes and mangroves. Such vegetation are considered “key ecosystems”, due to the connectivity with adjacent ecosystems, providing optimal functionality, and still favoring a multitude of organisms and people who use them. Aim of the study was to evaluate the level of knowledge and environmental perception about coastal vegetation (i.e., mangroves, saltmarshes and apicum) among visitors to the northern region of the Brazil. The semi-structured questionnaire used was divided into three parts related to: I) personal information, II) behavior in relation to the observed environmental problems, and III) ecological perception of these problems. A total of 70 people answered the online questionnaire, among which 50% are frequent users of the beaches in the north of Brazil, 35.7% rarely go there, and 14.5% have never been to the north coast. The results show that a significant portion of the people interviewed on the north coast was unaware of educational actions to avoid or minimize environmental impacts on the beaches, especially for vegetated habitats. Keywords: improper disposal; sandy beaches; faunal associations; environmental education; Amazon coast

Introduction

Coastal zone is characterized by high exchange between adjacent systems (e.g., mainland, fluvial zones, estuaries and the sea), where the mixture of dissolved materials promote high productivity in the different available habitats and consequently diverse ecological services to the fauna (SCHMIEGELOW, 2004; FRANCO et al., 2007; FONTELES-FILHO, 2011). This perspective makes us believe that biodiversity patterns are static and stable, however, small variations can significantly affect the establishment of the community and consequently its final biodiversity (PETCHEY; GASTON, 2002; COX; MOORE, 2013; MAGNUSSON et al., 2016).

The Brazilian coastline has an extension of ~ 7 408 km, characterized by the heterogeneity and complexity of ecosystems that can vary between rocky shores, bays, estuaries, cliffs, islands, among others, occupied by a floristic diversity linked to the morphostratigraphic characteristics of the different local and/or regional depositional environments (SCHAEFFER-NOVELLI, 1989; CIMA, 1991; BERRÊDO et al., 2008; FONTELES-FILHO, 2011; SANTOS et al., 2016).

According to SCHAEFFER-NOVELLI (1989), Brazilian coastal plant formations are characterized mainly by areas of apicum, salt marshes and mangrove forests. Apicuns are transitional arboreal vegetation and/or succession of mangroves, resulting from the deposition of sand, usually presenting hypersaline soils. While the marshes are specific herbaceous vegetation (i.e., belonging to the genus Spartina), exposed to the coastline in punctual intertidal patches (SCHAEFFER-NOVELLI, 1989; SCHMIDT et al., 2013). Mangrove forests are found in tropical and subtropical coastal regions, occupying saline or brackish muddy environments governed by the tidal cycle, yet they are recognized for their ecological importance as a nursery for several species, however, this is only one of the services offered (FAUNCE; SERAFY, 2006; MENEZES et al., 2008; MENEZES; MEHLIG, 2009). Such vegetation, mainly mangroves, are considered “key ecosystems” by many institutions (e.g., Mundial Banc – BIRD and FAO), due to connectivity with adjacent ecosystems providing its optimal functionality (SCHAEFFER-NOVELLI, 1989; FAO, 2017). However, despite approximately 75% of mangroves being present in various parts of the globe (i.e., 15 countries), only 6.9% of these forests are protected by the network of protected areas and at least 50% of them have already been lost (IUCN I-IV; KELLEHER et al., 1995; GIRI et al., 2011). FAO (2017), consider that the degradation of these vegetation can provide a significant increase in the probability of extreme weather events turning into disasters for the affected communities and the economy, especially with regard to the sustainability of food systems and the ability to meet their food demands.

In Brazil, the first protective norm for mangrove areas, for example, dates from February 4, 1577, a Regime edited by the Portuguese Crown so that tannin extraction (substance taken from the bark of mangrove trees, responsible for dyeing fabrics and leather) did not suffer scarcity (ICMBIO, 2018). The law 12,651 of 2012 conferred the title of permanent preservation areas to mangroves and sandbanks -APP (ICMBIO, 2018). However, these areas were severely impacted by anthropic actions, especially the mangroves, to the detriment of port developments, disordered urban growth, tourism, agriculture, aquaculture and industry, with emphasis on the northeast and southeast regions of Brazil (SCHAEFFER-NOVELLI, 1989; MENEZES; MEHLIG, 2009; ICMBIO, 2018; PELAGE et al., 2019). So far, the Amazonian mangroves can be considered preserved in relation to other regions, a fact that is probably due to the great distances and the difficult access to the interior of these (MENEZES et al., 2008; MENEZES; MEHLIG, 2009).

Studies involving Brazilian coastal vegetation, especially mangroves, are generally focused on biological or biogeochemical processes related to distribution patterns of organisms and flora, or even ecological modeling and local management (SCHAEFFER-NOVELLI, 1989; BERRÊDO et al., 2008). In this context, this study aimed to evaluate the level of knowledge and environmental perception about coastal vegetation (i.e., mangroves, saltmarshes, and apicum) among visitors to the northern region of Brazil. We believe that people's conscious relationship with the environment is a permanent and constant process that encompasses values, knowledge, experiences and determination to solve and/or avoid environmental problems in a way that they do not affect or influence their community (MACEDO et al., 2003; FERREIRA et al., 2020).

Methods

The coastal strip of the Northern Brazilian region extends from the Oiapoque Bay (northern end of the Amapá; 4°26'N and 51°31'W) at the mouth of the Gurupi river (northern end of the Pará; 1°05'S and 46°03'W), making up about ~ 964 km of coastline in a straight line, intersected by estuaries and bays. This region is characterized by the semidiurnal macrotidal regime (ranges up 4 to 7.5 m), subject to well-defined seasons, such as the wet season from January to June (> 2300 mm) and a dry period from July to December (< 50 mm), and average air temperatures around 26°C (SOUZA-FILHO, 2005; INMET, 2021). Such characteristics favor the culture of recreational tourism on this coast in its ~ 448 beaches (415 beaches with attractive potential in the state of Pará and 33 in Amapá, mainly during the dry season in the region (SANTOS et al., 2016; SETUR, 2021).

The northern coastal region of Brazil is densely occupied by several plant species, such as: mangroves (Rhizophora mangle, R. racemosa, R. harrisonii, Avicennia germinans, A. schaueriana, and Laguncularia racemosa, the saltmarshes (Spartina alterniflora and S. brasiliensis), transition plants (Sporobolus virginicus, Mandevilla sp.) between others (for more details see MENEZES et al., 2008).

The semi-structured questionnaire used was divided into three parts related to: I) personal information, II) behavior in relation to the observed environmental problems, and III) ecological perception of these problems. It was made available from January to July 2022 through an online electronic form through social networks or email (platform Google Forms; GOOGLE, 2022).

Results

A total of 70 people answered the online questionnaire, among which 50% (35 people) are frequent users of the beaches in the north of Brazil, 35.7% (25 people) rarely visit, and 14.5% (10 people) had never been to the north coast. There were 19 beaches (Figure 1) distributed in six host cities, namely: Macapá – AP, Belém – PA (Islands of Outeiro, Cotijuba and Mosqueiro), Marajó Island- PA, Marudá – PA, Salinópolis - PA, and Bragança – PA (Figure 2).

Figure 1 - Location of beaches frequently used for recreational purposes by respondents on the northern Brazilian coast. Beach locations are indicated by numbers: 1 – Fazendinha (Macapá), 2 – Joanes, 3 – Pesqueiro (Marajó Island), 4 – Vai quem quer (Cotijuba Island), 5- Amor (Outeiro Island), 6 – Prainha, 7 – Farol, 8 – Chapeu Virado, 9 – Murubira, 10 – São Francisco, 11 – Maraú, 12 – Paraiso (Mosqueiro Island), 13 – Marudá, 14 – Princesa (Algodoal Island), 15 – Corvina, 16 – Maçarico, 17 – Farol Velho, 18 – Atalaia (Salinópolis), and 19 – Ajuruteua (Bragança).

Figure 2 - Main cities that host the beaches frequented by respondents on the northern Brazilian Coast (percentage), 2022.

As for the general profile of respondents, 43 (61.4%) are female and 27 (38.6%) male. Considering the level of education, respondents with complete higher education predominated (64.3%, 45 users), followed by incomplete higher education (12.9%, 9), complete secondary education (11.4%, 8), incomplete secondary education (2.9%, 2), and others (8.6%, 6).

Beach users interviewed pointed out garbage as the main common problem on frequented beaches, followed by sewage and lack of infrastructure near or on the beach, such as bathrooms (Table 1). Additionally, those who answered “others”, specifically pointed out the absence of measures for ecological preservation and the permission for vehicle traffic inside the beach (i.e., Atalaia Beach) as worrying observations. Still, 84.3% of respondents said they were unaware of any educational actions for the environment in the municipality where the beach is located, and that they feel very dissatisfied (84.1%) in relation to the garbage observed on the beaches they frequent (Table 2).

Table 1 - Main problems of the beaches of Northern Brazil according to interviewed people, 2022.

Main problems

Number of observation (%)

Litter

56 (80%)

Wastewater

41 (58.6%)

Lack of infrastructure

36 (51.4%)

Toilet facilities

32 (45.7%)

Occupations (disordered dwellings)

23 (32.9%)

Domestic animals

20 (28.6%)

Other

4 (5.7%)



Table 2 - People behavior and perception in relation to litter contamination and the environment on the northern Brazilian Coast, 2022.

Questions

Answers

Number (%)

Do you know of environmental education actions that are developed in this municipality?

Yes

7 (10)

No

59 (84.3)

Maybe

4 (5.7)

How do you feel about the amount of garbage you see on the beach that you usually go to?

Unsatisfied

57 (81.4)

Pouco satisfeito

9 (12.9)

Satisfied

1 (1.4)

Very satisfied

2 (2.9)

I do not know

1 (1.4)

Is there coastal vegetation on the beach you visit?

Yes

46 (65.7)

No

6 (8.6)

I do not know

18 (25.7)

Do you know or know what mangroves, marshes and apicuns are?

Yes

33 (47.1)

No

17 (24.3)

Maybe

20 (28.6)

Have you ever visited the interior of one of these vegetated ecosystems?

Yes

24 (34.3)

No

41 (58.6)

Maybe

5 (7.1)

Do you often consume foods such as shrimp, crabs, turus, and fish when you go to the coast?

Yes

52 (74.3)

No

13 (18.6)

Maybe

5 (7.1)



When questioned about the garbage produced during the visit to the beach, the vast majority (94.3%) say they separate the garbage in their own bag to be discarded at the end, followed by (7.1%) those who leave the garbage with someone to be discarded (Figure 3).

Figure 3 - People behavior and perception in relation to litter contamination on the northern Brazilian Coast, 2022.

Coastal vegetation was noted by 65.7% of beach users, however only 47.1% said they recognized mangrove, saltmarsh and apicum vegetation (Table 2). Additionally, the vast majority (58.6%) have never visited the interior of these environments, but they frequently consume (74.3%) shrimp, crabs, turus and fish (Table 2).



Discussion

In this study, 70 people kindly answered the online questionnaire, showing themselves to be extremely concerned about the changes in the landscape of the beaches on the north coast of Brazil. It is worth noting that the sample was mostly composed of people with a higher level of education (higher education), a fact that biased the analysis towards a greater understanding of the anthropogenic impacts on coastal vegetation. Such environmental modifications, to the detriment of the forms of use by society, and their effects that were previously restricted to the local or regional scale, are gaining more and more global scales, drastically modifying the climate, ecosystems and consequently the patterns of biodiversity (MEINE, 2010; COELHO, 2020). In this context, environmental education aims to involve citizens in environmentally correct actions, preferably aiming to care for nature, through debates and conferences that assume not only an educational and environmental bias, but also a social and, above all, political one (DA-SILVA-ROSA et al., 2015; FERREIRA et al., 2020). It is worth noting that approximately 75% of respondents have completed or incomplete higher education, which leads us to believe that they may have already had access to information relevant to environmental impacts and/or measures to mitigate these impacts.

Nineteen beaches along the north coast were highlighted by the interviewees, where we can see that most of them are close to the capitals (i.e., Macapá – Amapá state and Belém – Pará state). The choice of beaches close to the users' cities of origin suggests an attempt to maximize their financial resources, where the savings achieved with the transfer, for example, can be invested with leisure activities and consumer goods on the destination beach (RABAHY et al., 2009). Additionally, because these beaches enter the Amazon estuary (i.e., greatly attenuated salinity), we observed a drastic change in plant characteristics, where restinga vegetation and herbaceous plants predominate, with mangrove vegetation being very punctual, however, still striking (for details see AMARAL et al., 2008; MENEZES et al., 2008).

The frequent presence of garbage on the beaches of the north coast was the main factor observed by the interviewed users, followed by sewage. This issue is already known and the subject of scientific and political discussions in various parts of the world, such as in South Africa (MADZENA; LASIAK, 1997; BALLANCE et al., 2000), Indonesia (WILLOUGHBY et al., 1997), United Kingdom (WILLIAMS; SIMMONS, 1997) and also in Brazil (SANTOS et al., 2005; ANDRADES et al., 2020). ANDRADES et al. (2020), highlighted the strong presence of plastic, cigarette butts, glass, metal and other materials present on the Brazilian coast, especially in the north. Furthermore, the north Brazilian coast is strongly influenced by the plume of the Amazon River and the north Brazilian current (CNB) (SILVA et al., 2005), a fact that would facilitate the dispersion of this garbage produced on our coast in various parts of the adjacent ocean. Studies already highlight that this garbage, especially plastic, once dispersed in the aquatic environment can affect all the fauna present (LI et al., 2016; VERMEIREN et al., 2016) and yet the man himself (CARBERY et al., 2018). This concern was demonstrated by users, when asked if they believed that this garbage could cause any problems for the beach, animals or people.

Yes, animals can be intoxicated with garbage, or even people/animals can be hurt by sharp objects, for example: beer bottle.”

Ignorance in any environmental educational actions was raised by 84.3% of respondents, and who still feel very dissatisfied with the garbage observed on the beaches where they frequent. One of the viable alternatives to raising society's awareness about the production of its solid waste and the consequent environmental, financial and social impact can be through advertising and education at all levels of education (MACIEL, 2020).

Another problem highlighted by users, specifically those who visit Farol Velho and Atalaia beaches in Salinópolis-PA, was the presence of car traffic on the beach, which would make adequate space for leisure, especially for children, unfeasible. Additionally, species belonging to infauna may suffer from these anthropic actions, due to major disturbances on the sediment leading to loss of habitats (LORENZI et al., 2023). The Brazilian Traffic Code (CTB) in the sole paragraph of article 2 of Law 9.503/97, defines what are considered land routes for public circulation, the beach is considered one of them. However, each municipality is able to define its own rules of use, thus safeguarding the natural features and protecting pedestrians (FONSECA, 2018). SCHERER (2013), points out that the main problems regarding beach management are generally associated with a lack of knowledge about the natural environment and the absence of citizen participation in decision-making.

The vast majority of users interviewed (i.e., 65.7%) claimed to be aware of the vegetation on the beaches they visit, however, only 47.1% know how to differentiate the vegetation of mangroves, marshes, apicuns, among others. Still, the majority stated that they had never visited the interior of these habitats, but that they frequently consume shrimp, crabs, turus and fish. The lack of knowledge about these vegetation’s is to make clear the lack of knowledge about the diversity in fauna and flora, their environmental, economic and social, direct and indirect values for society (SCHAEFFER-NOVELLI, 1989). In the case of mangroves, for example, formality is waived as a conservation unit, since it is already considered an ecosystem destined for permanent preservation (article 2, Federal Law No. 4,771 of 9/15/65) and as an Ecological Reserve, “in all its extension” (articles 1° and 3°, Resolution of CONAMA N° 004, September 18, 1985) (SCHAEFFER-NOVELLI, 1989). However, even so, in mid-2020 the Brazilian Ministry of the Environment tried to extinguish this protection, putting natural resources in check due to industrial activities (SHALDERS, 2020; MELO, 2021). The loss of this habitat (e.g., mangrove suppression on a stretch of Maçarico beach, in Salinópolis-PA, for the construction of a seafront; Figure 4) would be harmful to a large population contingent that uses the mangroves as a means of subsistence or to obtain income, through the extraction of animals such as mollusks (mussels, oysters, turus) and crustaceans (shrimp of various species, crabs and uçá-crab) (MENEZES; MEHLIG, 2009; DIAS et al., 2022).

Figure 4 - Mangrove suppression on a stretch of Maçarico beach, in Salinópolis-PA, 2023 (Photo: Authors, December 28, 2023).

Conclusion

In conclusion, this study shows that a significant portion of the users of beaches on the north coast interviewed were unaware of educational actions to avoid or minimize environmental impacts on beaches, mainly for vegetated habitats. However, they showed great concern with all environmental disturbances:

Make more trash cans available and greater action by bar owners to collect or inform their customers to keep their garbage to be collected when they leave.”

I think that the long-term solution would be to include a regular subject of Environmental Education in the school curriculum, from primary school to the end of high school. Thus, we would have the formation of an environmental conscience in the future frequenter of these places. But, right now, there needs to be more campaigns to hold people accountable on the beaches and more government oversight, as well as tougher fines for those who degrade the coastal environment.”

Some measures to mitigate the impacts of solid waste on beaches could involve interactive activities with local residents (e.g., lectures, distribution of pamphlets with information on the issue of waste to human and animal health), the availability of an adequate number of accessible waste bins, as well as their regular maintenance. In addition to awareness campaigns that highlight the potential dangers associated with garbage for visitors, the use of security cameras, designed to catch potential polluters so that they can be fined. Additionally, it is worth noting that the relationship between man and the environment is constant, so actions involving society and public policies aimed at conservation and sustainability are necessary and necessary for a good coexistence in nature.



References

AMARAL, Dário Dantas do; PROST, Maria Thereza; BASTOS, Maria de Nazaré do Carmo; NETO, Salustiano Vilar Costa; SANTOS, João Ubiratan Moreira dos. Restingas do litoral amazônico, estados do Pará e Amapá, Brasil. Boletim do Museu Paraense Emílio Goeldi - Ciências Naturais, v. 3, n. 1, p. 35–67, 2008. Available on-line at https://repositorio.museu-goeldi.br/handle/mgoeldi/1467

ANDRADES, Ryan; PEGADO, Tamyris; Godoy, BRUNO S.; et al. Anthropogenic litter on Brazilian beaches: Baseline, trends and recommendations for future approaches. Marine Pollution Bulletin, v. 151, p. 110842, 2020. https://doi.org/10.1016/j.marpolbul.2019.110842

BALLANCE, A; RYAN, PG; TURPIE, JK. How much is a clean beach worth? The impact of litter on beach users in the Cape Peninsula, South Africa. South African Journal of Science, v. 96, n. 5, p. 210–213, 2000. https://doi.org/10.10520/AJA00382353_8975

BERRÊDO, José Francisco, COSTA, Marcondes Lima da; VILHENA, Maria do Perpétuo Socorro Progene; SANTOS, Josiana Torres. Mineralogia e geoquímica de sedimentos de manguezais da costa amazônica: o exemplo do estuário do rio Marapanim (Pará). Revista Brasileira de Geociências, v. 38, n. 1, p. 24–35, 2008. Available on-line at https://repositorio.ufpa.br/bitstream/2011/6461/1/Artigo_MineralogiaGeoquimicaSedimentos.pdf

CARBERY, Maddison; O’CONNOR, Wayne; PALANISAMI, Thavamani. Trophic transfer of microplastics and mixed contaminants in the marine food web and implications for human health. Environment International, v. 115, p. 400–409, 2018. https://doi.org/10.1016/j.envint.2018.03.007

CIMA. Subsídios técnicos para elaboração do relatório nacional do Brasil para a Conferência das Nações Unidas sobre Meio Ambiente e Desenvolvimento. 171 p., Brasília, Comissão Interministerial para a preparação da preparação a Conferência das Nações Unidas sobre Meio Ambiente e Desenvolvimento, 1991.

COELHO, Andréa dos Santos. Agenda internacional para o desenvolvimento sustentável. In: MARTINS, Marlúcia Bonifácio. et al. (Org.). Reflexões em Biologia da Conservação. Belém: Museu Paraense Emílio Goeldi. pp. 53–72, 2020. ISBN 978-85-61377-97-7. Available on-line at https://repositorio.museu-goeldi.br/bitstream/mgoeldi/1508/1/reflexoes-em-biologia-da-conservacao_v1.pdf

COX, C. Barry; MOORE, Peter D. Biogeografia: uma abordagem ecológica e evolucionária. 398 p. 7, 2013. Ed. Livros Técnicos e Científicos Editora Ltda. ISBN: 978-85-216-1663-4

DA-SILVA-ROSA, Teresa. et al. A educação ambiental como estratégia para a redução de riscos socioambientais. Ambiente & Sociedade, v. 18, n. 3, p. 211–230, 2015. https://doi.org/10.1590/1809-4422ASOC1099V1832015

DIAS, Rubens Ramos; ROCHA, Filipe de Melo; MARTINELLI-LEMOS, Jussara Moretto; OLIVEIRA, Rory Romero de Sena; Oliveira, Danielly Brito de. Caracterização socioeconômica da atividade pesqueira do Caranguejo-uçá em uma RESEX da Amazônia Brasileira. Revista Caparaó, v. 4, n. 2, p. e76, 2022. Available on-line at https://www.revistacaparao.org/caparao/article/view/76.

FAO. The future of food and agriculture – Trends and challenges. 180 p. 2017. Rome.

FAUNCE, Craig H.; SERAFY, Joseph E. Mangroves as fish habitat: 50 Years of field studies. Marine Ecology Progress Series, v. 318, p 1–18, 2006. https://doi.org/10.3354/meps318001

FERREIRA, Ananda Paula Rodrigues F et al. A Educação Ambiental como Ferramenta na Formação e no Exercício da Cidadania. In: BRITO, Daguinete Maria Chaves; SILVA, Eliane Aparecida Cabral da, LANDIM-NETO, Francisco Otávio. (Org.). Educação Ambiental no cotidiano: ações de proteção ambiental. p. 9–24, 2020. Available on-line at https://www2.unifap.br/editora/files/2020/09/educacao-ambiental-no-cotidiano.pdf#page=10

FONSECA, Gustavo. Como funciona a fiscalização de veículos nas praias? In: <https://jus.com.br/artigos/66786>. Accessed in: Ago 4, 2022.

FONTELES-FILHO, Antonio Adauto. Oceanografia, biologia e dinâmica populacional de recursos pesqueiros. Expressão Gráfica e Editora. 464 p, 2011. ISBN: 978.85.7563.789.0

FRANCO, Anita; TORRICELLI, Patrizia; ELLIOTT, Michael. Preface: Biodiversity and ecosystem functioning in coastal and transitional waters. Edited by Anita Franco, Michael Elliott and Patrizia Torricelli. Estuarine, Coastal and Shelf Science, v. 75, n. 1–2, p. 1–3, 2007. https://doi.org/10.1016/j.ecss.2007.05.013

GIRI, C.; OCHIENG, E.; TIESZEN, L. L.; ZHU, Z.; SINGH, A.; LOVELAND, T.; MASEK, J.; DUKE, N. Status and distribution of mangrove forests of the world using earth observation satellite data. Global Ecology and Biogeography, v. 20, n. 1, p. 154–159, 2011. https://doi.org/10.1111/j.1466-8238.2010.00584.x

GOOGLE. Clear Google Drive space & increase storage. 2022. Available in: https://www.google.com.br/drive/apps.html. Accessed in: July 31, 2023.

Instituto Chico Mendes de Conservação da Biodiversidade (ICMBIO). Atlas dos manguezais do Brasil. Ministério do Meio Ambiente. 176 p, 2018.

INMET. Normas Climatológicas (2020–2021). Instituto Nacional de Meteorologia, Brasília, DF. Available in: https://portal.inmet.gov.br/normais. Accessed in: January 17, 2023.

LI, Wai Chin; HUNG Fat Tse; LINCOLN, Fok. Plastic waste in the marine environment: A review of sources, occurrence and effects. Science of the Total Environment, v. 566–567, p. 333–349, 2016. https://doi.org/10.1016/j.scitotenv.2016.05.084

LORENZI, Luciano; MAYER, Devon Gebauer; REGINATO, Bruna Conte; PAGLIOSA, Paulo Roberto; DANTAS, David Valença; GENTIL, Eduardo; VALENCIA, Vladimir G. Toro. Relationships between benthic infauna and groundwater eutrophication on a sandy beach in Southern Brazil. Environmental Science and Pollution Research, v. 30, n. 4, p. 10841–10853, 2023. https://doi.org/10.1007/s11356-022-22853-9

MACEDO, Renato Luiz Grisi; NAPPO, Mauro Elói; BARREIRA, Sybelle; VIVETTE, Appolinário. Enquete ambiental entre universitários de cursos de Ciências Agrárias. Revista Científica Eletrônica de Engenharia Florestal, v. 1, n. 1, p. 1–4, 2003. Available on-line at https://faef.revista.inf.br/imagens_arquivos/arquivos_destaque/hres6gLasqhGs2g_2013-4-24-14-16-7.pdf

MACIEL, Vinícius Queiroz. Consumismo: do copo descartável à pegada ecológica. In: MARTINS, Marlúcia Bonifácio; JARDIM, Mário Augusto Gonçalves; SABINO, William de Oliveira, BARROS, Maria Fabíola Gomes da Silva de (Org.). Reflexões em Biologia da Conservação. p. 41–49, 2020. Available on-line at https://repositorio.museu-goeldi.br/handle/mgoeldi/1508

MADZENA, Azwifarwi; LASIAK, Theresa. Spatial and Temporal Variations in Beach Litter on the Transkei Coast of South Africa. Marine Pollution Bulletin, v. 34, n. 11, p. 900–907, 1997. https://doi.org/10.1016/S0025-326X(97)00052-0

MAGNUSSON, William Ernest; ISHIKAWA, Noemia Kazue; LIMA, Albertina Pimentel; et al. A linha de véu: a biodiversidade brasileira desconhecida. Parcerias Estratégicas, v. 21, n. 42, p. 45-60, 2016. Available on-line at https://cdi.mecon.gob.ar/bases/doc/parceriasest/42.pdf#page=47

MEINE, Curt. Conservation biology: past and present. In: SODHI, NS; EHRLICH, Paul R. (Org.). Conservation Biology for All. 6. ed. New York: Oxford University Press. pp. 7–22, 2010. ISBN: 978-0-19-955423-2

MELO, Aline. Do litoral norte ao sul: manguezais sofrem com atividade humana. Diário de Pernambuco, 2021. Available in: <https://www.diariodepernambuco.com.br/noticia/brasil/2021/06/do-litoral-norte-ao-sul-manguezais-sofrem-com-atividade-humana.html#:~:text=Com o desmatamento da vegetação,pesqueiros no litoral do estado.>. Accessed in: January 17, 2023.

MENEZES, Moirah Paula Machado De; MEHLIG, Ulf. Manguezais: As florestas da Amazônia costeira. Ciência Hoje, v. 44, n. 264, p. 34–39, 2009. Available in: <https://cienciahoje.org.br/artigo/manguezais-as-florestas-da-amazonia-costeira/>

Menezes, Moirah Paula Machado De; Berger, Uta; Mehlig, Ulf. Mangrove vegetation in Amazonia: A review of studies from the coast of Pará and Maranhão States, north Brazil. Acta Amazonica, v. 38, n. 3, p. 403–419, 2008. https://doi.org/10.1590/S0044-59672008000300004

PELAGE, Latifa; DOMALAIN, Gilles; LIRA, Alex S.; et al. Coastal Land Use in Northeast Brazil: Mangrove Coverage Evolution Over Three Decades. Tropical Conservation Science, v. 12, p. 1940082918822411, 2019. https://doi.org/10.1177/19400829188224

PETCHEY, Owen L.; GASTON, Kevin J. Functional diversity (FD), species richness and community composition. Ecology Letters, v. 5, p. 402–411, 2002. https://doi.org/10.1046/j.1461-0248.2002.00339.x

RABAHY, Wilson Abrahão; SANTOS, Glauber Eduardo de Oliveira; VASSALLO, Moisés Diniz. Determinantes do gasto em viagens turísticas domésticas no Brasil. Turismo - Visão e Ação, v. 11, n. 3, p. 304–324, 2009. Available in: <http://www6.univali.br/seer/index.php/rtva/article/view/644>.

SANTOS, Valdenira Ferreira dos; SHORT, Andrew D.; MENDES, Amilcar Carvalho. Beaches of the amazon coast: Amapá and West Pará. In: SHORT, Andrew D.; KLEIN, ntonio Henrique da F. (Org.). Brazilian Beach Systems: Review and Overview. Springer, Cham. 17: 67–93, 2016. ISBN: 978-3-319-30394-9

SANTOS, Isaac Rodrigues; FRIEDRICH, Ana Claúdia; WALLNER-KERSANACH, Mônica; FILLMANN, Gilberto. Influence of socio-economic characteristics of beach users on litter generation. Ocean & Coastal Management, v. 48, p. 742–752, 2005. https://doi.org/10.1016/j.ocecoaman.2005.08.006

SCHAEFFER-NOVELLI, Yara. Situação atual do grupo de ecossistemas: “Manguezal, Marisma e Apicum” incluindo os principais vetores de pressão e as perspectivas para sua conservação e usos sustentável. Brasília: Agência Nacional de Petróleo, Gás Natural e Biocombustíveis, 1989. Available on-line at https://www.gov.br/anp/pt-br/brnd/round6/guias/PERFURACAO/PERFURACAO_R6/refere/manguezal_marisma_apicum.pdf

SCHERER, Marinez. Gestão de Praias no Brasil: Subsídios para uma Reflexão. Revista de Gestão Costeira Integrada, v. 13, n. 1, p. 3–13, 2013. Available on-line at https://www.redalyc.org/pdf/3883/388340140001.pdf

SCHMIDT, Anders Jensen; BEMVENUTI, Carlos Emílio; DIELE, Karen. Sobre a definição da zona de apicum e a sua importância ecológica para populações de caranguejo-uçá, Ucides cordatus. Boletim Técnico-Científico do CEPENE, v. 19, n. 1, p. 9–25, 2013. Available on-line at https://www.icmbio.gov.br/cepene/images/stories/publicacoes/btc/vol19/art01-v19.pdf

SCHMIEGELOW, João Marcos Miragaia. O planeta azul: uma introdução às ciências marinhas. Rio de Janeiro: Interciência, 202 p, 2004. ISBN: 85-7193-102-X

SETUR. Secretária de Turismo do Pará. Available on-line at <http://setur.pa.gov.br/>. Accessed in: December 28, 2021.

SHALDERS, André. Por que decisão de Ricardo Salles sobre manguezais representa “volta no tempo” de quase 500 anos. BBC News/Brasil, Out 2020. Available on-line at <https://www.bbc.com/portuguese/brasil-54461270>.

SILVA, Alex Costa da; ARAÚJO, Moacyr; BOURLÈS, Bernard. Variação sazonal da estrutura de massas de água na plataforma continental do Amazonas e área oceânica adjacente. Revista Brasileira de Geofísica, v. 23, v. 2, p. 145–157, 2005. https://doi.org/10.1016/j.rsma.2017.08.012

SOUZA-FILHO, Pedro Walfir Martins. Costa de Manguezais de macromaré da Amazônia: Cenários morfológicos, mapeamento e quantificação de áreas usando dados de sensores remotos. Revista Brasileira de Geofísica, v. 23, n. 4, p. 427–435, 2005. https://doi.org/10.1590/S0102-261X2005000400006

VERMEIREN, Peter; MUÑOZ, Cynthia C.; IKEJIMA, Kou. Sources and sinks of plastic debris in estuaries: A conceptual model integrating biological, physical and chemical distribution mechanisms. Marine Pollution Bulletin, v. 113, n. 1–2, p. 7–16, 2016. https://doi.org/10.1016/j.marpolbul.2016.10.002

WILLIAMS, AT; SIMMONS, SL. Estuarine Litter at the River/Beach Interface in the Bristol Channel, United Kingdom. Journal of Coastal Reseach, v. 13, n. 4, p. 1159–1165, 1997. Available on-line at https://www.jstor.org/stable/4298724

WILLOUGHBY, NG; SANGKOYO, Hendro; LAKASERUS, Boyke O. Beach Litter: an Increasing and Changing Problem for Indonesia. Marine Pollution Bulletin, v. 34, n. 6, p. 469-478, 1997. https://doi.org/10.1016/S0025-

Ilustrações: Silvana Santos